CN113956015A - Household garbage incineration ash concrete and preparation method thereof - Google Patents
Household garbage incineration ash concrete and preparation method thereof Download PDFInfo
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- CN113956015A CN113956015A CN202111392769.9A CN202111392769A CN113956015A CN 113956015 A CN113956015 A CN 113956015A CN 202111392769 A CN202111392769 A CN 202111392769A CN 113956015 A CN113956015 A CN 113956015A
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B28/00—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
- C04B28/24—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing alkyl, ammonium or metal silicates; containing silica sols
- C04B28/26—Silicates of the alkali metals
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2111/00—Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
- C04B2111/00017—Aspects relating to the protection of the environment
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2111/00—Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
- C04B2111/00474—Uses not provided for elsewhere in C04B2111/00
- C04B2111/00767—Uses not provided for elsewhere in C04B2111/00 for waste stabilisation purposes
- C04B2111/00775—Uses not provided for elsewhere in C04B2111/00 for waste stabilisation purposes the composition being used as waste barriers or the like, e.g. compositions used for waste disposal purposes only, but not containing the waste itself
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2201/00—Mortars, concrete or artificial stone characterised by specific physical values
- C04B2201/50—Mortars, concrete or artificial stone characterised by specific physical values for the mechanical strength
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- Structural Engineering (AREA)
- Organic Chemistry (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The invention provides incineration ash concrete of household garbage and a preparation method thereof, belonging to the technical field of solid waste resource utilization. In the domestic garbage incineration ash concrete provided by the invention, the crude slag and the fine slag are prepared from domestic garbage incineration slag, and the modified fly ash sand and the modified fly ash are prepared from domestic garbage incineration fly ash, so that the troubles of occupation of the domestic garbage incineration ash and land pollution can be solved, waste materials are changed into valuable, natural sandstone resources and cementing materials can be saved, and the finally prepared domestic garbage incineration ash concrete can meet the use requirements of non-structural concrete. The results of the examples show that the strength of the household garbage incineration ash concrete provided by the invention is 22.8-34.1 MPa after standard maintenance for 28 days, and the leaching results of all heavy metal ions are qualified.
Description
Technical Field
The invention relates to the technical field of solid waste resource utilization, in particular to domestic garbage incineration ash concrete and a preparation method thereof.
Background
The municipal solid waste incineration treatment is widely applied due to obvious reduction, harmlessness and resource advantages, and the municipal solid waste incineration treatment can generate domestic waste incineration ash residues comprising domestic waste incineration slag and domestic waste incineration fly ash, wherein the domestic waste incineration slag accounts for about 20% of the total mass of the domestic waste, and the domestic waste incineration fly ash accounts for about 5% of the total mass of the domestic waste.
At present, domestic waste incinerator slag disposal is mainly for stabilizing post-sanitary landfill, but with the gradual shortage of land resources, the sanitary landfill capacity is continuously reduced, and the domestic waste incinerator slag is subjected to the trouble of being placed everywhere due to the restriction of factors such as difficult site selection of a newly-built landfill site and the like.
The fly ash from incineration of municipal solid waste is definitely classified as dangerous waste, which contains heavy metals and dioxin-like substances with high concentration, and if the fly ash is not disposed well, the fly ash will cause serious harm to the ecological environment. At present, the treatment modes of the household garbage incineration fly ash mainly comprise cement solidification and stabilization, a chemical treatment method, a safe landfill method and the like, but the problems of high treatment cost and great technical difficulty are generally existed.
Therefore, how to economically and effectively treat the household garbage incineration ash to prevent the household garbage incineration ash from polluting the environment becomes a hot spot of social attention and research.
Disclosure of Invention
The invention aims to provide the domestic garbage incineration ash concrete and the preparation method thereof, the domestic garbage incineration ash concrete is prepared based on the domestic garbage incineration ash, the troubles of occupation and land pollution of the domestic garbage incineration ash can be solved, waste is changed into valuable, meanwhile, natural sandstone resources and cementing materials can be saved, and the concrete has obvious environmental benefit and economic benefit.
In order to achieve the above object, the present invention provides the following technical solutions:
the invention provides household garbage incineration ash concrete which comprises the following preparation raw materials in parts by weight:
450-550 parts of coarse furnace slag, wherein the particle size of the coarse furnace slag is 4.75-26.5 mm;
360-440 parts of fine slag, wherein the particle size of the fine slag is less than 4.75 mm;
20-60 parts of modified fly ash sand, wherein the particle size of the modified fly ash sand is 0.075-4.75 mm;
11-30 parts of modified fly ash, wherein the particle size of the modified fly ash is less than 0.075 mm;
110-150 parts of mineral powder;
25-45 parts of water glass;
1.2-2.5 parts of sodium hydroxide;
60-75 parts of water;
wherein the coarse slag and the fine slag are obtained by crushing and screening household garbage incinerator slag;
the preparation method of the modified fly ash sand and the modified fly ash comprises the following steps:
mixing the household garbage incineration fly ash, glass powder and limestone powder and then calcining to obtain a calcined material; and sequentially dechlorinating, crushing and screening the calcined material to obtain the modified fly ash sand and the modified fly ash.
Preferably, the mass ratio of the household garbage incineration fly ash to the glass powder to the limestone powder is (3-5): (3-5): (1-2).
Preferably, the particle size of the glass frit is <0.15 mm.
Preferably, the particle size of the limestone powder is <0.075 mm.
Preferably, the calcining temperature is 800-1000 ℃ and the calcining time is 1-3 h.
Preferably, the dechlorination mode is water washing; and (3) on the basis of dry mass, the mass content of chloride ions in the washed material is less than or equal to 0.02% by water washing.
Preferably, the ore powder is S95 grade ore powder or S105 grade ore powder.
Preferably, the modulus of the water glass is 3.1-3.3.
The invention provides a preparation method of the domestic garbage incineration ash concrete in the technical scheme, which comprises the following steps:
mixing coarse slag, fine slag, modified fly ash sand, modified fly ash, mineral powder, water glass, sodium hydroxide and water to obtain a primary material;
and forming and maintaining the primary material to obtain the household garbage incineration ash concrete.
Preferably, the mixing manner of the coarse slag, the fine slag, the modified fly ash sand, the modified fly ash, the mineral powder, the water glass and the sodium hydroxide with water comprises the following steps:
firstly mixing water glass, sodium hydroxide and water to obtain a liquid material;
performing second mixing on the coarse slag, the fine slag, the modified fly ash sand, the modified fly ash and the mineral powder to obtain a solid material;
and carrying out third mixing on the liquid material and the solid material to obtain a primary material.
The invention has the following beneficial effects:
(1) according to the invention, the coarse slag and the fine slag are prepared from the household garbage incineration slag, and the modified fly ash sand and the modified fly ash are prepared from the household garbage incineration fly ash, so that the troubles of occupation and land pollution of the household garbage incineration slag can be solved, waste materials are changed into valuable, natural sandstone resources and cementing materials can be saved, and the finally prepared household garbage incineration slag concrete can meet the use requirements of non-structural concrete.
(2) The household garbage incinerator slag is loose and porous, and can play a good role in adsorbing and fixing heavy metals; compared with cement-based cementing materials, the alkali-activated cementing material has better heavy metal curing effect.
(3) When the modified fly ash sand and the modified fly ash are prepared by using the household garbage incineration fly ash, the problem of leaching of toxic and harmful heavy metal ions in the household garbage incineration fly ash is solved through calcination and dechlorination, and meanwhile, the modified fly ash sand and the modified fly ash have the volcanic ash activity, so that the modified fly ash sand and the modified fly ash become qualified concrete mineral admixtures.
(4) The invention innovatively and completely uses the household garbage incineration ash as the concrete aggregate, innovatively uses the household garbage incineration fly ash to prepare the modified fly ash sand, replaces part of fine aggregate, improves the use amount of the household garbage incineration fly ash in the concrete and simultaneously reduces the leaching amount of heavy metal ions.
The results of the examples show that the strength of the household garbage incineration ash concrete provided by the invention is 22.8-34.1 MPa after standard maintenance for 28 days, and the leaching results of all heavy metal ions are qualified.
Detailed Description
The invention provides household garbage incineration ash concrete which comprises the following preparation raw materials in parts by weight:
450-550 parts of coarse furnace slag, wherein the particle size of the coarse furnace slag is 4.75-26.5 mm;
360-440 parts of fine slag, wherein the particle size of the fine slag is less than 4.75 mm;
20-60 parts of modified fly ash sand, wherein the particle size of the modified fly ash sand is 0.075-4.75 mm;
11-30 parts of modified fly ash, wherein the particle size of the modified fly ash is less than 0.075 mm;
110-150 parts of mineral powder;
25-45 parts of water glass;
1.2-2.5 parts of sodium hydroxide;
60-75 parts of water;
wherein the coarse slag and the fine slag are obtained by crushing and screening household garbage incinerator slag;
the preparation method of the modified fly ash sand and the modified fly ash comprises the following steps:
mixing the household garbage incineration fly ash, glass powder and limestone powder and then calcining to obtain a calcined material; and sequentially dechlorinating, crushing and screening the calcined material to obtain the modified fly ash sand and the modified fly ash.
According to the weight parts, the raw materials for preparing the incineration ash concrete of the household garbage comprise 450-550 parts of coarse slag, preferably 500-500 parts of coarse slag; the particle size of the coarse slag is 4.75-26.5 mm; the bulk density is preferably 1100 to 1200kg/m3More preferably 1180kg/m3。
On the basis of the mass parts of the coarse slag, the raw materials for preparing the domestic garbage incineration ash concrete comprise 360-440 parts of fine slag, preferably 360-400 parts of fine slag; particle size of the fine slag<4.75 mm; the bulk density is preferably 1300 to 1400kg/m3More preferably 1350kg/m3。
In the invention, the coarse slag and the fine slag are obtained by crushing and screening the household garbage incineration slag. The source of the household garbage incineration slag is not specially limited, and particularly the slag at the bottom of the furnace after the household garbage incineration; in an embodiment of the invention, the domestic waste incinerator slag is from a Shenzhen domestic waste power plant. The specific mode of crushing and screening is not particularly limited, and coarse slag and fine slag meeting the particle size requirements can be obtained.
In the invention, the household garbage incinerator slag is loose and porous, can play a good role in adsorbing and fixing heavy metals, and the coarse slag and the fine slag prepared from the household garbage incinerator slag are used as concrete aggregates, so that waste can be changed into valuable, and natural sandstone resources are saved.
On the basis of the mass parts of the coarse slag, the raw materials for preparing the incineration ash slag concrete of the household garbage comprise 20-60 parts of modified fly ash sand, preferably 20-40 parts of modified fly ash sand; the particle size of the modified fly ash sand is 0.075-4.75 mm; the bulk density is preferably 960 to 1040kg/m3More preferably 1000kg/m3。
Based on the mass parts of the coarse slag, the raw materials for preparing the incineration ash concrete of the household garbage comprise 11-30 parts of modified fly ash, preferably 20-30 parts of modified fly ash; the particle size of the modified fly ash<0.075mm, and the preferable specific surface area is 350-400 m2/g。
In the invention, the preparation method of the modified fly ash sand and the modified fly ash comprises the following steps:
mixing the household garbage incineration fly ash, glass powder and limestone powder and then calcining to obtain a calcined material;
and sequentially dechlorinating, crushing and screening the calcined material to obtain the modified fly ash sand and the modified fly ash.
The method mixes the household garbage incineration fly ash, the glass powder and the limestone powder and then calcines the mixture to obtain a calcined material. The source of the household garbage incineration fly ash is not particularly limited, and particularly the fly ash is collected in a flue after the household garbage is incinerated; in the embodiment of the invention, the household garbage incineration fly ash is from a Shenzhen household garbage power plant. In the present invention, the glass frit is preferably made from crushed glass powder, the particle size of the glass frit is preferably <0.15 mm; the particle size of the limestone powder is preferably less than 0.075 mm. In the invention, the mass ratio of the household garbage incineration fly ash, the glass powder and the limestone powder is preferably (3-5): (3-5): (1-2), more preferably 3: 3: 1. in the invention, the calcining temperature is preferably 800-1000 ℃, and more preferably 950 ℃; the time is preferably 1 to 3 hours, and more preferably 2 hours. In the invention, the glass powder is used as a heavy metal flux after being melted so as to achieve the purpose of solidifying heavy metals, and the limestone powder is used as a flux.
In the present invention, the calcination preferably further includes cooling; the cooling method of the present invention is not particularly limited, and a cooling method known to those skilled in the art may be used. In the invention, the block or granular substance is obtained after cooling, namely the calcined material.
After the calcined material is obtained, the calcined material is sequentially dechlorinated, crushed and screened to obtain the modified fly ash sand and the modified fly ash. In the present invention, the dechlorination method is preferably water washing; and the washing is preferably carried out by taking the mass content of chloride ions in the washed material to be less than or equal to 0.02 percent as a reference by dry mass, and the standard requirement of concrete structure engineering construction specification GB50666-2011 is met. In the present invention, it is preferable to further include drying after the water washing, and the drying is not particularly limited in the present invention, and sufficient drying can be achieved. The specific mode of crushing and screening is not particularly limited, and modified fly ash sand and modified fly ash meeting the particle size requirements can be obtained.
The invention innovatively and completely uses the household garbage incineration ash as the concrete aggregate, innovatively uses the household garbage incineration fly ash to prepare the modified fly ash sand, replaces part of fine aggregate, improves the use amount of the household garbage incineration fly ash in the concrete and simultaneously reduces the leaching amount of heavy metal ions.
Based on the mass parts of the coarse slag, the raw materials for preparing the incineration ash concrete of the household garbage comprise 110-150 parts of mineral powder, preferably 130-150 parts. In the invention, the ore powder is preferably S95 grade ore powder or S105 grade ore powder. In the invention, the mineral powder is activated by alkaline substances to generate gelation.
Based on the mass parts of the coarse slag, the raw material for preparing the incineration ash concrete of the domestic garbage comprises 25-45 parts of water glass, and preferably 35-45 parts. In the invention, the modulus of the water glass is preferably 3.1-3.3, and more preferably 3.2. In the invention, the water glass is used as an excitant to excite the activity of the mineral powder.
Based on the mass parts of the coarse slag, the raw materials for preparing the incineration ash concrete of the household garbage comprise 1.2-2.5 parts of sodium hydroxide, preferably 2-2.5 parts. In the invention, the sodium hydroxide is preferably industrial-grade flaky sodium hydroxide with the purity of more than or equal to 99 percent. In the invention, the sodium hydroxide is used for exciting the activity of the mineral powder.
Based on the mass parts of the coarse slag, the raw material for preparing the incineration ash concrete of the household garbage comprises 60-75 parts of water, preferably 68-75 parts of water.
The strength of the household garbage incineration ash concrete after standard curing for 28 days is 22.8-34.1 MPa, the use requirement of non-structural concrete can be met, and the leaching result of each heavy metal ion is qualified.
The invention provides a preparation method of the domestic garbage incineration ash concrete in the technical scheme, which comprises the following steps:
mixing coarse slag, fine slag, modified fly ash sand, modified fly ash, mineral powder, water glass, sodium hydroxide and water to obtain a primary material;
and forming and maintaining the primary material to obtain the household garbage incineration ash concrete.
The method mixes coarse slag, fine slag, modified fly ash sand, modified fly ash, mineral powder, water glass, sodium hydroxide and water to obtain a primary material. In the present invention, the mixing manner of the coarse slag, the fine slag, the modified fly ash sand, the modified fly ash, the mineral powder, the water glass, and the sodium hydroxide with water preferably includes:
firstly mixing water glass, sodium hydroxide and water to obtain a liquid material;
performing second mixing on the coarse slag, the fine slag, the modified fly ash sand, the modified fly ash and the mineral powder to obtain a solid material;
and carrying out third mixing on the liquid material and the solid material to obtain a primary material.
In the present invention, the first mixing is preferably performed under stirring conditions, and the stirring rate and time are not particularly limited in the present invention, and sodium hydroxide may be completely dissolved. In the present invention, the system exotherms during said first mixing, preferably by cooling to obtain a liquid mass.
In the present invention, the second mixing is preferably performed in a concrete mixer, and the time for the second mixing is preferably 30 to 60 seconds, and more preferably 45 to 60 seconds.
In the present invention, the third mixing is preferably performed by adding the liquid material to the solid material, the third mixing is preferably performed in a concrete mixer, and the time of the third mixing is preferably 240 to 300 seconds, and more preferably 270 to 300 seconds.
After the primary material is obtained, the primary material is molded and maintained to obtain the incineration ash concrete of the household garbage. The present invention is not particularly limited to the molding and curing, and may be carried out in a manner known to those skilled in the art. In the embodiment of the invention, the initial material is filled into a concrete mould, inserted and tamped or vibrated, and demoulded after being cured at room temperature to obtain the incineration ash concrete of the household garbage; in the present invention, the room temperature curing time is preferably 24 hours.
The technical solution of the present invention will be clearly and completely described below with reference to the embodiments of the present invention. It is to be understood that the described embodiments are merely exemplary of the invention, and not restrictive of the full scope of the invention. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present invention.
The source and index parameters of raw materials for preparing the domestic garbage incineration ash concrete in the following examples are as follows:
crushing and screening the household garbage incinerator slag (from Shenzhen household garbage power plant) to obtain coarse slag and fine slag; the particle size of the coarse slag is 4.75-26.5 mm, and the bulk density is 1180kg/m3(ii) a Particle size of the fine slag<4.75mm, a bulk density of 1350kg/m3；
The method comprises the following steps of (1) burning fly ash of the domestic garbage (from Shenzhen domestic garbage power plant), glass powder and limestone powder according to the mass ratio of 3: 3: 1, calcining for 2 hours at 950 ℃, and cooling to obtain a calcined material; washing the calcined material with water until the mass content of chloride ions is not more than 0.02% (calculated by dry mass), and then drying, crushing and screening the calcined material in sequence to obtain modified fly ash sand and modified fly ash; wherein the glass powder is prepared by grinding glass cullet and has a particle size<0.15 mm; the particle size of the limestone powder<0.075 mm; particle size of the modified fly ash sand<4.75mm, bulk density 1000kg/m3(ii) a The particle size of the modified fly ash<0.075mm, and the specific surface area of 350-400 m2/g；
Mineral powder: s95 grade mineral powder;
water glass: the modulus is 3.2;
sodium hydroxide: the purity of industrial-grade flaky sodium hydroxide is more than or equal to 99 percent.
Example 1
Mixing 1.2 parts of sodium hydroxide, 25 parts of water glass and 60 parts of water in parts by weight, stirring to dissolve the sodium hydroxide, and cooling to obtain a liquid material;
adding 450 parts of coarse slag, 440 parts of fine slag, 60 parts of modified fly ash sand, 11 parts of modified fly ash and 110 parts of mineral powder into a concrete mixer, and stirring for 30s to obtain a solid material;
adding the liquid material into a solid material, and stirring for 240s in the concrete mixer to obtain a primary material;
and putting the primary material into a concrete mold, compacting, curing at room temperature (20 +/-5 ℃) for 24 hours, and then demolding to obtain the household garbage incineration ash concrete.
Example 2
Mixing 2 parts of sodium hydroxide, 35 parts of water glass and 68 parts of water in parts by weight, stirring to dissolve the sodium hydroxide, and cooling to obtain a liquid material;
adding 500 parts of coarse slag, 400 parts of fine slag, 40 parts of fly ash sand, 20 parts of fly ash and 130 parts of mineral powder into a concrete mixer and stirring for 45s to obtain a solid material;
adding the liquid material into a solid material, and stirring in the concrete mixer for 270s to obtain a primary material;
and putting the primary material into a concrete mold, compacting, curing at room temperature (20 +/-5 ℃) for 24 hours, and then demolding to obtain the household garbage incineration ash concrete.
Example 3
Mixing 2.5 parts of sodium hydroxide, 45 parts of water glass and 75 parts of water in parts by weight, stirring to dissolve the sodium hydroxide, and cooling to obtain a liquid material;
adding 550 parts of coarse slag, 360 parts of fine slag, 20 parts of fly ash sand, 30 parts of fly ash and 150 parts of mineral powder into a concrete mixer, and stirring for 60s to obtain a solid material;
adding the liquid material into a solid material, and stirring for 300s in the concrete mixer to obtain a primary material;
and putting the primary material into a concrete mold, compacting, curing at room temperature (20 +/-5 ℃) for 24 hours, and then demolding to obtain the household garbage incineration ash concrete.
The municipal solid waste incineration ash concrete prepared in examples 1 to 3 was subjected to standard curing (at 20 ℃ and a relative humidity of 95% or more) for 28 days, and then the obtained concrete sample was subjected to a performance test, specifically as follows:
testing the strength of the concrete sample according to GB/T50081-2019 concrete physical and mechanical property test method standard;
the leaching amount of the heavy metal ions in the concrete sample is tested according to GB/T30810-.
The test results are shown in Table 1.
Table 1 results of performance test of concrete containing incineration ash of domestic waste prepared in examples 1 to 3
As can be seen from table 1, the leaching results of each heavy metal ion in the incineration ash concrete of domestic garbage prepared in examples 1 to 3 were all qualified; the strength of the household garbage incineration ash concrete prepared in the embodiment 1 is 22.8MPa after standard curing for 28 days, and the strength requirement of RC20 concrete can be met; the strength of the household garbage incineration ash concrete prepared in the embodiment 2 is 27.7MPa after standard curing for 28 days, and the strength requirement of RC25 concrete can be met; the strength of the domestic garbage incineration ash concrete prepared in the embodiment 3 is 34.1MPa after standard curing for 28 days, and the strength requirement of RC30 concrete can be met.
The foregoing is only a preferred embodiment of the present invention, and it should be noted that, for those skilled in the art, various modifications and decorations can be made without departing from the principle of the present invention, and these modifications and decorations should also be regarded as the protection scope of the present invention.
Claims (10)
1. The household garbage incineration ash concrete comprises the following preparation raw materials in parts by weight:
450-550 parts of coarse furnace slag, wherein the particle size of the coarse furnace slag is 4.75-26.5 mm;
360-440 parts of fine slag, wherein the particle size of the fine slag is less than 4.75 mm;
20-60 parts of modified fly ash sand, wherein the particle size of the modified fly ash sand is 0.075-4.75 mm;
11-30 parts of modified fly ash, wherein the particle size of the modified fly ash is less than 0.075 mm;
110-150 parts of mineral powder;
25-45 parts of water glass;
1.2-2.5 parts of sodium hydroxide;
60-75 parts of water;
wherein the coarse slag and the fine slag are obtained by crushing and screening household garbage incinerator slag;
the preparation method of the modified fly ash sand and the modified fly ash comprises the following steps:
mixing the household garbage incineration fly ash, glass powder and limestone powder and then calcining to obtain a calcined material; and sequentially dechlorinating, crushing and screening the calcined material to obtain the modified fly ash sand and the modified fly ash.
2. The household garbage incineration ash concrete according to claim 1, wherein the mass ratio of the household garbage incineration ash, the glass powder and the limestone powder is (3-5): (3-5): (1-2).
3. The household garbage incineration ash concrete according to claim 1 or 2, characterized in that the particle size of the glass powder is <0.15 mm.
4. The municipal solid waste incineration ash concrete according to claim 1 or 2, wherein the limestone powder has a particle size of <0.075 mm.
5. The concrete of incineration ash of household garbage according to claim 1, wherein the temperature of calcination is 800 to 1000 ℃ and the time is 1 to 3 hours.
6. The municipal solid waste incineration ash concrete according to claim 1, wherein the dechlorination means is water washing; and (3) on the basis of dry mass, the mass content of chloride ions in the washed material is less than or equal to 0.02% by water washing.
7. The concrete of municipal solid waste incineration ash according to claim 1, wherein the ore fines are grade S95 ore fines or grade S105 ore fines.
8. The concrete of municipal solid waste incineration ash according to claim 1, wherein the modulus of the water glass is 3.1 to 3.3.
9. The method for producing the concrete of incineration ash of domestic garbage according to any one of claims 1 to 8, comprising the steps of:
mixing coarse slag, fine slag, modified fly ash sand, modified fly ash, mineral powder, water glass, sodium hydroxide and water to obtain a primary material;
and forming and maintaining the primary material to obtain the household garbage incineration ash concrete.
10. The method of claim 9, wherein the coarse slag, the fine slag, the modified fly ash sand, the modified fly ash, the mineral powder, the water glass, and the sodium hydroxide are mixed with water in a manner comprising:
firstly mixing water glass, sodium hydroxide and water to obtain a liquid material;
performing second mixing on the coarse slag, the fine slag, the modified fly ash sand, the modified fly ash and the mineral powder to obtain a solid material;
and carrying out third mixing on the liquid material and the solid material to obtain a primary material.
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN115385622A (en) * | 2022-07-12 | 2022-11-25 | 河海大学 | Solid waste pavement repairing material and preparation method thereof |
| CN115819002A (en) * | 2022-11-10 | 2023-03-21 | 山东高速股份有限公司 | Slag fine aggregate of household garbage incinerator and preparation method and application thereof |
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|---|---|---|---|---|
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
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| CN115385622A (en) * | 2022-07-12 | 2022-11-25 | 河海大学 | Solid waste pavement repairing material and preparation method thereof |
| CN115385622B (en) * | 2022-07-12 | 2023-05-16 | 河海大学 | Solid waste pavement repairing material and preparation method thereof |
| CN115819002A (en) * | 2022-11-10 | 2023-03-21 | 山东高速股份有限公司 | Slag fine aggregate of household garbage incinerator and preparation method and application thereof |
| CN115819002B (en) * | 2022-11-10 | 2023-08-15 | 山东高速股份有限公司 | Household garbage incinerator slag fine aggregate and preparation method and application thereof |
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| CN113956015B (en) | 2022-07-15 |
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